1
Waterbirds in the UK 2014/15 The annual report of the Wetland Bird Survey
in association with
Waterbirds in the UK 2014/15
2
WATERBIRDS IN THE UK 2014/15 The Wetland Bird Survey (WeBS) is the principal scheme for monitoring the UK’s wintering waterbird populations, providing an important indicator of their status and the health of wetlands. Waterbirds in the UK 2014/15 is the 34th WeBS annual report and comprises this summary report and data at www.bto.org/webs-reporting. British Trust for Ornithology The Nunnery
The Wetland Bird Survey (WeBS) is run by the British Trust for Ornithology (BTO). It is a partnership funded by the BTO, the Royal Society for the Protection of Birds (RSPB) and the Joint Nature Conservation Committee (JNCC) (the last on behalf of the statutory nature conservation agencies: Natural England, Natural Resources Wales and Scottish Natural Heritage and the Department of the Environment Northern Ireland), in association with the Wildfowl & Wetlands Trust (WWT). The permanent members of the WeBS Steering Committee in 2014/15 were Chas Holt (BTO), Andy Musgrove (BTO), David Stroud (JNCC), Simon Wotton (RSPB) and Richard Hearn (WWT).
Thetford Norfolk IP24 2PU
THE WeBS TEAM AT BTO
www.bto.org
Joint Nature Conservation Committee
THE WeBS PARTNERSHIP
Monkstone House City Road Peterborough PE1 1JY
www.jncc.defra.gov.uk
Teresa Frost - WeBS National Coordinator Heidi Mellan - Counter Network Organiser Neil Calbrade - Low Tide Count Organiser Graham Austin - Database Manager Dave Turvey - Web Software Developer Dawn Balmer - Head of Surveys Email: firstname.surname@bto.org
Royal Society for the Protection of Birds
General enquiries to WeBS:
WeBS, BTO, The Nunnery, Thetford, Norfolk IP24 2PU
The Lodge Sandy Bedfordshire SG19 2DL
Email: webs@bto.org Tel: 01842 750050
www.rspb.org.uk
Wildfowl & Wetlands Trust Slimbridge Gloucestershire GL2 7BT
www.wwt.org.uk
WeBS website: www.bto.org/webs Other contacts: Goose & Swan Monitoring Programme - organised and funded by WWT, JNCC and SNH. Email: monitoring@wwt.org.uk Other national waterbird surveys - details of (and contacts for) other waterbird surveys can be obtained via the websites of the WeBS partner organisations.
ACKNOWLEDGEMENTS We are indebted to the time and skills of the thousands of WeBS Counters who collected the data used in this report and to the invaluable efforts of the WeBS Local Organisers who are listed on the back cover. The WeBS Local Organiser Advisory Committee (LOAC) (members listed on page 39) provided advice on behalf of counters and Local Organisers. The BTO Information Systems team delivered essential technical assistance and continues to develop and provide assistance for WeBS Online. Chas Holt left the WeBS team in spring 2015 and we thank him for all his work developing and managing WeBS over the past seven years.
We are also grateful to the following for providing supplementary information, data inputting, proof-reading and particularly invaluable help in 2014/15: Niall Burton, Mark Eaton, GSMP, Colette Hall, Jane Herridge, Maria Knight, Tom Langendoen, Nick Lewis, John Marchant, Veronica Mendez, Richard Minter, Andy Musgrove, Deborah Proctor, RAFOS, Marc van Roomen, Kathryn Ross and SOTEAG. Grateful thanks to all and apologies to anyone who has been inadvertently missed. Report content and production was by Teresa Frost, Dawn Balmer and Neil Calbrade, with assistance on layout from Sarah Harris. The article on waterbird monitoring in Finland was contributed by Aleksi Lehikoinen.
The painting of Mallards, used on the cover of this report, is by Colin Blanchard. For more of Colin's work, see www.colinblanchard.com. All other artists and photographers are acknowledged on the pages of this report.
Maps in this report contain Ordnance Survey data Š Crown Copyright and database right 2016. This report was printed by Swallowtail Print.
Waterbirds in the UK 2014/15
3
CONTENTS...
p.4
p.34
Waterbird Headlines.....................4
Habitat Focus............................16
Species Focus...............................32
The Online Reporting Interface...5
International.............................. 22
Species Focus...............................33
Species in the news in 2014/15. An overview of the online WeBS reporting interface.
The WeBS Year..............................6 Coverage and weather in 2014/15.
Population Trends......................10 National trends for waterbirds wintering in the UK in 2014/15.
Principal Sites............................12 Sites with the largest aggregations of wintering waterbirds. SHELDUCK BY JILL PAKENHAM, RED-NECKED GREBE BY DAVE KING, SPOTTED REDSHANK BY TOM BICKERTON, HAYLE ESTUARY BY DAWN BALMER
p.28
p.14
BoCC4.......................................14 An overview of changes in the Birds of Conservation Concern list.
The UK's natural still water habitats.
A detailed look at Crane in the UK.
Waterbird monitoring and research in the East Atlantic flyway.
A detailed look at Shoveler in the UK.
Another National Scheme......... 24
The Low Tide Count scheme in 2014/15.
Waterbird monitoring scheme in Finland.
Stratified Population Estimates.26 Using the distribution of wetland habitats for estimating waterbird populations.
Species Focus...............................28
Low Tide Counts........................34
Uses of WeBS Data.....................38 Review of how WeBS data were utilised in 2014/15.
WeBS Local Organisers..............39
A detailed look at scarcer winter waders.
A list of WeBS Local Organisers and members of the WeBS LOAC.
Species Focus..............................30
Special Thanks............back cover
A detailed look at Bar-tailed Godwit in the UK.
CITATION Frost, T.M., Austin, G.E., Calbrade, N.A., Holt, C.A., Mellan, H.J., Hearn, R.D., Stroud, D.A., Wotton, S.R. & Balmer, D.E. 2016. Waterbirds in the UK 2014/15: The Wetland Bird Survey. BTO, RSPB and JNCC, in association with WWT. British Trust for Ornithology, Thetford. Published by the British Trust for Ornithology, Royal Society for the Protection of Birds and Joint Nature Conservation Committee, in association with Wildfowl & Wetlands Trust, May 2016. Principal Sites Table (page 13) revised June 2016. Š British Trust for Ornithology, Royal Society for the Protection of Birds and Joint Nature Conservation Committee, in association with Wildfowl & Wetlands Trust, 2016. ISBN 978-1-908581-66-2
Online Resources More information, including site tables and trends for all regular WeBS species, is available online at www.bto.org/webs-reporting. This summary report can be downloaded from the WeBS website at www.bto.org/webspublications. The online and summary outputs in conjunction constitute the report Waterbirds in the UK 2014/15.
Headline Stories
Waterbird headlines from the WeBS-year Just a small selection of notable stories from 2014/15 See all the numbers and trends at www.bto.org/webs-reporting
COOT: RIC JACKSON
The birds most frequently recorded on a WeBS count tend to be widespread species that are recorded all year round. The top 10 most recorded species were Mallard (present on 27,637 WeBS sector core count visits between July 2014 and June 2015), Mute Swan (17,940), Black-headed Gull (17,624), Moorhen (16,601), Coot (16,346), Cormorant (14,786), Tufted Duck (14,561), Grey Heron (14,548), Teal (11,847) and Canada Goose (11,218). Some of the most ubiquitous waterbirds are the most challenging when it comes to estimating nonbreeding populations. New research into using habitat classes to produce estimates for such species is reported on pages 26–27 and emphasises the value of counts from small waterbodies as well as large ones. Pages 16–21 focus on some ubiquitous birds of inland still freshwaters – Mute Swan, Moorhen and Tufted Duck.
The winter weather of 2014/15 was fairly typical for the UK and the recent series of typical maritime mild winters appears to have allowed recovery in species such as Little Grebe. News from waterbird monitoring in Finland shows a general trend for waterbirds making use of Finnish wetlands in winter as milder winters become more frequent (pages 24–25). Some of the scarcer waders in winter have seen UK mid-winter numbers increase (pages 28–29) – could this be climate related? Shoveler responds rapidly to weather drivers and is another species that is increasing (page 33) as is Crane, which is being given a helping hand through a reintroduction project (page 32).
Data on non-breeding waterbirds from the Wetland Bird Survey is essential for assessing species status. UK WeBS trends for many estuarine species such as Shelduck, Curlew, Redshank, Dunlin and Oystercatcher have shown steady declines, whereas the UK indices for some fish-eating species such as Little Egret have increased rapidly in the past 25 years. An East Atlantic Flyway-wide assessment finds a similar pattern (pages 22–23). Bar-tailed Godwit is a coastal species with a more stable long-term trend (pages 30–31). Many coastal species are red-listed in the latest UK’s Birds of Conservation Concern (pages 14–15). Pochard has also joined the red-list due to its ongoing decline, with the overwinter trend in the UK decreasing by two thirds between 1987/88 and 2013/14.
LITTLEGREBE: LIZ CUTTING
OYSTERCATCHER: JILL PAKENHAM
4
Online Reporting Interface 5
WeBS Report Online Explore species trends, peak counts and more at www.bto.org/webs-reporting
This annual report, Waterbirds in the UK 2014/15, is the fourth in the revised format that combines an extensive online data resource (WeBS Report Online) with this summarised written report. The WeBS Report Online interface provides access to the latest tables of WeBS Core Count data at site and species level via the 'Numbers and Trends' tab, together with low tide summaries and distribution density maps for certain sites via the ‘Low Tide Counts’ tab. In the ‘Numbers and Trends’ section, selecting their site of interest from the menu allows users to explore which species have ever been recorded at the site. Users can see the peak numbers of each species recorded at the site throughout the year, the five-year mean peak count and the month in which the peak count was recorded. The table can be sorted alphabetically or taxonomically by species or by the peak counts. By scrolling back through the years, contemporary
counts and associated five-year averages can be compared with historical counts at the site. For those looking for information on a particular species (or biogeographic population) of waterbird, every species ever recorded by WeBS features on its own page, with every site where the species has been recorded listed. As well as offering the functionality to sort sites in tables either alphabetically, by annual peak, or by five-year average, the interface also allows the user to filter sites by country, county and/or habitat. This useful feature is appreciated by scientists, conservationists, county bird recorders and amateur enthusiasts alike. Annual and monthly trend plots for the UK and constituent countries are shown (where applicable) and there are also links to other sources of web-based information - helping to make WeBS Report Online a comprehensive data
portal for anyone with an interest in the UK's waterbirds. Supplementary counts can be included or excluded in the tables. For reference purposes, data from annual reports for previous years can be accessed by choosing the appropriate WeBS year from the ‘Waterbirds in the UK’ drop-down menu. Whilst not part of the WeBS annual report, WeBS Report Online also includes the latest available information on the status of waterbirds at Special Protection Areas and Sites of Special Scientific Interest that are designated for their waterbird features via the ‘WeBS Alerts’ tab. Future additions may include sections to report results from periodic surveys such as NEWS (Non-Estuarine Waterbird Survey). WeBS Report Online, launched in 2014, continues to be a significant success and is recognised as one of the major achievements of the JNCC/BTO 2010 – 2016 Partnership.
FIND OUT MUCH MORE... Access WeBS Report Online at www.bto.org/webs-reporting The Numbers & Trends section features species trends (for the UK and constituent countries) and site tables for all species (with facility to filter by country, county and habitat), alongside sections on Low Tide Counts and WeBS Alerts. There is also a Help section containing tutorials, to help you make the most of the resource.
The WeBS year
2014/15: WeBS Core Count coverage continues to grow
3,130 regis
tered WeBS volunte ers
WeBS CORE COUNTS Core Counts were carried out at a record 5,292 WeBS sectors (count units) at 2,799 sites from July 2014 to June 2015. Not all Core Counts are linked to individual counters in the WeBS Online database, but an increasing number are; 2,031 counters were associated with WeBS Core Count visits made in 2014/15, an increase of 5% on the previous year. Core Count dates in 2014/15 2014 13 July 10 August 7 September 12 October 9 November 7 December
2015 18 January 8 February 8 March 19 April 17 May 14 June
6,000
5,000
4,000 Number of sectors
3,000
2,000
1,000
0
2005/06 2006/07 2007/08 2008/09 2009/10 2010/11 2011/12 2012/13 2013/14 2014/15
Numbers of WeBS Count sectors covered 2005/06 to 2014/15.
WeBS LOW TIDE COUNTS WeBS Low Tide Counts were carried out on 16 estuaries in 2014/15. This included coverage of some irregularly covered sites such as the Dee Estuary
(Cheshire/Clwyd), Hamford Water (Essex), Alt Estuary (Merseyside), Kent and Wyre Estuaries (Lancashire) and Portsmouth Harbour (Hampshire).
A review of the WeBS Low Tide Counts scheme in 2014/15 can be found on pages 34–36.
GOOSE CENSUSES Many populations of wintering geese were censused using other surveys. Counts of Taiga Bean Geese were provided by the Bean Goose Action Group (Slamannan Plateau) and RSPB (Middle Yare Marshes). Surveys of Pink-footed and Icelandic Greylag Geese were undertaken at, primarily, roost sites in October to December 2014 as part of the Icelandic-breeding Goose Census. British Greylag Geese at key sites in Scotland were censused by a number of local management groups, including the Uist Greylag Goose Management Committee.
Greenland White-fronted Geese were monitored by the Greenland Whitefronted Goose Study. Greenland Barnacle Geese were counted by SNH on Islay and other key locations, while WWT counted Svalbard Barnacle Geese on the Solway. Data were also provided by the International Canadian Light-bellied Brent Goose census. For progress reports on goose censuses in the UK, see GooseNews, WWT’s annual newsletter of the Goose & Swan Monitoring Programme. Further goose and swan information is available via http://monitoring.wwt.org.uk.
JOHN DUNN
6
Light-bellied Brent Goose numbers have shown a long-term increase in the UK.
The WeBS Year 7
WeBS coverage in 2014/15 Counts were carried out at 2,799 wetlands across the UK in 2014/15. Areas shown in black were counted at least once - providing a picture of the excellent geographical coverage achieved.
For sites covered by I-WeBS in Ireland, please see the I-WeBS pages at
birdwatchireland.ie Also check p.27 of Waterbirds in the UK 2011/12 for a detailed review of I-WeBS.
The WeBS year
2014/15: a warm autumn and typical winter The 2014/15 UK winter saw a typical number of days with air frost and temperatures near average. Higher than usual rainfall in northwest Scotland and Northern Ireland contrasted with drier than usual conditions in the east, a pattern that continued in spring. The following 2014/15 weather summary is collated from the Meteorological Office website at www.metoffice.gov.uk. July 2014 saw widespread warmer than average temperatures. South-west Britain received below average rainfall, but localised downpours gave above average rainfall in East Anglia. In contrast to the preceding eight months, which had all been warmer than average, August was the coolest since 1993, with early ground frosts in the second half of the month. The remnant of Hurricane Bertha brought high winds and heavy rain to many areas. The unsettled weather resulted in 155% of typical August rainfall. A return to fine and settled conditions throughout September gave rainfall of only 24% of the 1981–2010 average for the month, but with temperatures returning to above normal.
Unsettled conditions returned in October with southerly winds bringing wet weather with few dry periods, although it was also warmer than average. The pattern of wet, windy, warm weather continued into November. The UK rainfall was 102% of average but this disguised double the average rainfall in parts of Northern Ireland, eastern Scotland and southern England whereas western and central Scotland, north-west England and north Wales were drier than usual. December saw unsettled weather from moist, warm Atlantic air flows alternating spells of cool and mild temperatures, dry and wet or snowy days. It was the second sunniest December since 1929. The first half of January 2015 was stormy, particularly in the north, and mild; whereas the second half was colder with frosts and some snow. Rainfall was above average. Temperatures in England and Wales were above average but were below average in Scotland and Northern Ireland. Rainfall was slightly below average for many areas in February. The month began with a cold northerly airflow,
followed by dry and quiet weather from 5th to 12th and then milder unsettled weather from the west. In March, south-eastern Britain and north-eastern Scotland had low rainfall but above average in northwest Scotland and average precipitation in-between meant the UK rainfall total was exactly equal to the 30-year mean. The weather was generally unsettled apart from a quieter spell mid-month. As April progressed the weather became more settled with some very warm weather mid-month; however the weather turned cold for the last week of April with some overnight frosts. Rainfall was 64% of average. The airflow was predominately northwesterly in May bringing wetter and cooler conditions than is typical. It was the fourth May out of the last five to be substantially wetter than average and the coldest since 1996. June was mostly rather cool, with unsettled conditions over Scotland but drier further south.
THE ARCTIC BREEDING SEASON Arctic breeding conditions for birds that winter in the UK are summarised from the International Breeding Conditions Survey on Arctic Birds, available from www. arcticbirds.net. Arctic spring in 2014 was generally late with cold, rainy and windy conditions reported from many stations. Overall bird breeding success was mostly reported to be average or unclear, with some stations mentioning reduced breeding success for insect-eating birds as a result of the poor weather. Rodent abundance was considered to be low or average across the majority of arctic regions where monitoring was undertaken. However, rodent numbers were high in Taimyr in northern Siberia, where it was noted that although usually this results in high wader breeding success due to reduced predation from Arctic Fox, in summer 2014 this effect was not seen and wader breeding success was believed to be low.
BEN GREEN
8
The peak count of Wood Sandpipers
in 2014/15 was six on the North Norfolk Coast in July.
LES FOSTER
General Background 9
WeBS objectives, aims and methods The Wetland Bird Survey (WeBS) monitors non-breeding waterbirds in the UK in order to provide the principal data on which the conservation of their populations is based. To this end, WeBS has three main objectives: - to assess the size of nonbreeding waterbird populations in the UK; - to assess trends in their numbers and distribution; and - to assess the importance of individual sites for waterbirds. These results also form the basis for informed decision-making by conservation bodies, planners and developers, and contribute to the sustainable use and management of wetlands and their dependent waterbirds. The data and this annual WeBS report also fulfil some of the objectives of relevant international Conventions and Directives to which the UK is a signatory. WeBS also provides data to Wetlands International to assist their function of coordinating and reporting upon waterbird status at an international flyway scale.
WeBS continues the traditions of two long-running count schemes which formed the mainstay of UK waterbird monitoring since 1947. WeBS Core Counts are carried out at a wide variety of wetlands. Coordinated, synchronous counts are advocated to prevent doublecounting or birds being missed. Priority dates are recommended nationally, but due to differences in tidal regimes around the UK, counts take place at some estuaries on other dates in order to match the most suitable local conditions. Weather and counter availability also sometimes result in counts being undertaken on alternative dates. In addition, WeBS Low Tide Counts are undertaken on selected estuaries with the aim of identifying key areas used during the low tide period, principally by feeding birds. It also identifies areas not otherwise noted for their importance from data collected during Core Counts which are normally conducted at, or close to, high tide.
The success and growth of these count schemes reflects the enthusiasm and dedication of the several thousands of participating volunteer ornithologists. It is largely due to their efforts that waterbird monitoring in the UK is held in such high regard internationally. Full details of WeBS field and analytical methodologies are available via the WeBS website: www.bto.org/webs. Waterbirds in the UK 2014/15 (comprising this summary report together with numbers and trends available from WeBS Report Online at www.bto.org/websreporting) presents the results of WeBS in 2014/15. Data from other national and local waterbird monitoring schemes, notably the WWT/JNCC/SNH Goose & Swan Monitoring Programme, are included where WeBS data alone are insufficient to fulfil specified aims. The annual WeBS report therefore provides a single, comprehensive source of information on waterbird status and distribution in the UK.
10 Population Trends
National trends A concise summary of how the UK’s most familiar waterbirds fared in 2014/15 GEESE & SWANS
The Mute Swan WeBS index has dropped slightly in the past few years but remains stable in the medium term (see pages 20–21). Whooper Swan numbers remain high and Bewick’s Swan low. Naturalised goose populations continued to increase with record or near record numbers of Barnacle, Egyptian, Canada and Greylag Geese. The picture for visiting wintering geese was more mixed. Another record high was set for Pinkfooted Geese and another record low for European White-fronted Geese. Numbers remained high for Svalbard and Greenland Barnacle Geese but Greenland White-fronted Geese continued their decline. Dark-bellied Brent Geese numbers increased by 25% compared with 2013/14 whereas both Nearctic and Svalbard Light-bellied Brent Geese continued a short-term decline.
DUCKS
There was a halt in the year-on-year decreases in the Shelduck index. Pintail numbers increased very slightly after declines were recorded in six of the past eight years, with a total now half that counted in 2005/06. Mallard numbers are now 7% higher than the all-time low recorded in 2012/13. Shoveler (see
page 33) and Teal numbers remained around historic highs as did Gadwall, despite being 15% lower than the 2011/12 peak. Red-breasted Merganser and Pochard numbers fell again slightly, continuing a pattern seen in 12 of the past 15 years for both species. Goosander and Tufted Duck (see pages 18–19) numbers remain stable and Goldeneye numbers were up slightly, but in the context of a 50% long-term decline.
WADERS
Long-term declining species Ringed Plover, Oystercatcher and Dunlin showed small year-on-year increases. Numbers of Lapwing returned to similar numbers to the past six years after the increase recorded in 2013/14, and Golden Plover was also down. Sanderling numbers were unchanged compared to the previous year. There are tentative signs that Redshank numbers are stabilising after a period of decline. However declines continued in Turnstone, Purple Sandpiper and Curlew, and Grey Plover numbers dropped again after a brief upturn. Ruff numbers were up, with the highest index for ten years (see pages 28–29).
Counts of Black-tailed Godwit and Avocet remain high and although Bartailed Godwit numbers dropped they were within the normal range for this species (see pages 30–31).
RAILS, GREBES & HERONS
The WeBS indices for Water Rail, Coot and Moorhen (see page 20) all increased in 2014/15 compared with 2013/14. Little Grebe numbers increased by 20% and are back to 2005/06 – 2009/10 levels, perhaps indicating recovery after the cold 2009/10 and 2010/11 winters. The Little Egret index continues to increase rapidly as the population range expands, with the number of birds reported from Scotland WeBS counts doubling compared with 2013/14. Wintering Grey Heron numbers appear to have increased for the second year after a period of decline.
GULLS
There is a sustained decline in the WeBS trends for Common, Blackheaded and Lesser Black-backed Gulls where the indices are a third to a half of those in the late 1990s. Shallower declines in Great Blackbacked and Herring Gulls also continued in 2014/15.
100
80
WeBS Index
60
40
0 90/91
95/96
00/01
05/06
10/11
WeBS trend for Little Egret in UK. Green dots = annual index value; blue line = smoothed trend.
15/16
ANDY MUSGROVE
20
Population Trends 11
Table 1 Population trends of non-breeding waterbirds in the UK Species/population
25-year trend (1988/89– 2013/14)
Mute Swan Bewick's Swan Whooper Swan
10-year trend Species/population (2003/04 –2013/14)
49
-8
1
-9
-60
Goldeneye
-50
-32
Red-breasted Merganser
-15
-20
20
12
n/a Ruddy
Duck
-99
-100
Little Grebe
98
-51 33
European White-fronted Goose -79
-47
Greenland White-fronted Goose -24
-41
Eider *
Goosander
n/a
-9
Great Crested Grebe
15
-22
Cormorant
60
0
1
-18
-26
-19
Icelandic Greylag Goose
-15
8
n/a
British Greylag Goose
149
31
n/a
Canada Goose
49
8
Greenland Barnacle Goose
188
59
Oystercatcher
Svalbard Barnacle Goose
210
35
Avocet
Dark-bellied Brent Goose
15
46
Ringed Plover
Canadian Light-b. Brent Goose 60
37
Svalbard Light-b. Brent Goose
77
-13
-28
-28
Wigeon
33
-16
Gadwall
170
15
52
1
Shelduck
Teal
10-year trend (2003/04 –2013/14)
-77 102
Pink-footed Goose
25-year trend (1988/89 –2013/14)
Coot
910
46
-60
-39
Golden Plover
96
-25
Grey Plover
-17
-11
Lapwing
14
-27
-12
-13
Knot Sanderling Purple Sandpiper
30
10
-59
-11
Mallard
-40
-17
Dunlin
-34
-23
Pintail
-41
-46
Black-tailed Godwit
335
45
Shoveler
68
5
Pochard
-65
-41
Tufted Duck Scaup
Bar-tailed Godwit
-3
-6
Curlew
-9
-12
10
9
Redshank
-23
-22
-34
-46
Turnstone
-46
-18
Trends are % changes, for the most abundant wildfowl and waders. The longer term smoothed trend refers to the 25 year period 1988/89 to 2013/14. The shorter term smoothed trend refers to the 10 year period 2003/04 to 2013/14. It is customary to calculate trends to an end-point of year (n-1) (where n = 2014/15). Preceding each species is an indication of international trend, based on: Nagy, S., Flink, S. & Langendoen, T. (2015) Sixth AEWA Report on the Conservation Status of Migratory Waterbirds in the Agreement Area. Wetlands Int., NL. increasing, decreasing, stable. *Eider trends exclude birds on Shetland (of faeroeensis race). Insufficient data series to calculate 25-year trend for Little Grebe.
DAVE WRAGG
Trends use WeBS data except for Pink-footed Goose, Greenland White-fronted Goose, Icelandic Greylag Goose, Greenland Barnacle Goose, Svalbard Barnacle Goose and Canadian Light-bellied Brent Goose, for which dedicated censuses are undertaken (see page 6).
Purple Sandpiper: down 59% since 1988/89.
For all trend graphs see the online report ...
www.bto.org/webs-reporting
12 Principal Sites
Largest waterbird aggregations Millions of waterbirds are dependent on the UK’s wetlands each winter This section of Waterbirds in the UK summarises the sites that support the largest aggregations of waterbirds each year. Understanding precisely how many individual birds use a site is clearly very difficult to ascertain from counts alone, as many sites are used by migrants on passage and consequently there can be high turnover rates. Current research uses colour-ringing and remote tracking technologies in order to improve knowledge of turnover rates. Table 2 lists the Principal Sites for non-breeding waterbirds in the UK as monitored by WeBS. The totals are the summed maxima for each species during the course of the WeBS year. Sites with a five-year average of 20,000+ waterbirds are listed. Nonnative species (e.g. Canada Goose and Ruddy Duck) have been excluded from the totals. Gulls and terns are also excluded since the recording of them during WeBS Counts is optional and thus they are inconsistently included in totals.
in 2009/10 no longer appearing in the table. The removal of the high count of 151,681 in 2009/10 from the five-year period and a lower-thanaverage year in 2014/15 has seen the Humber Estuary fall two places in the Principal Sites table. Numbers at many of the top sites were lower in 2014/15 than they were in 2013/14, only the Dee Estuary and Somerset Levels recording an increase between years. The Somerset Levels
20,000 - 30,000 30,000 - 50,000 50,000 - 75,000 75,000 - 100,000 >100,000
total was the highest there since the hard winter of 2010/11. Outside of the top ten sites, Montrose Basin and Blackwater Estuary both featured notable totals in 2014/15. Lower than expected totals at some sites are partially attributable to missing counts for key species in certain months.
1) The Wash 2) Ribble Estuary 3) Morecambe Bay 4) Thames Estuary 5) North Norfolk Coast 6) Dee Estuary 7) Solway Estuary 8) Humber Estuary 9) Somerset Levels 10) Breydon Water & Berney Marshes 11) Alt Estuary 12) Ouse Washes 13) Montrose Basin 14) Mersey Estuary 15) Severn Estuary
A total of 53 WeBS sites in 2014/15, one more than in 2013/14, had a fiveyear average of over 20,000 waterbirds. Typically, there are few changes between years to the top sites listed in the Principal Sites table, and the order of the most important sites tends to remain largely unchanged between years. However, several sites across the UK experienced changes of greater than 10% between 2013/14 and 2014/15, which were probably attributable to variation in weather conditions between the two winters affecting use of some sites more than others.
SITE FOCUS
The Wash remains the premier site for wintering waterbirds in the UK. This is despite the five-year average reducing by 18,000 birds, from 366,094 in 2013/14 to 348,097 in 2014/15, due to the record high count
Largest waterbird aggregations in the UK. Sites are those listed in Table 2, with top fifteen sites labelled on the map.
Principal Sites 13
Table 2 Principal Sites for non-breeding waterbirds in the UK Site
2010/11
2011/12
2012/13
2013/14
2014/15
5-year mean
The Wash
358,651
294,609
350,031
393,260
343,932
348,097
Ribble Estuary
204,741
259,990
178,318
174,200
171,680
197,786
Morecambe Bay
239,424
201,581
191,056
181,689
171,968
197,144
152,995 152,161 179,961 194,525 168,515
169,631
205,471 158,303 121,563 153,506 121,195
152,008
Thames Estuary
North Norfolk Coast
Dee Estuary (England and Wales)
118,107
120,763
151,290
124,605
136,507
130,254
Solway Estuary
149,697
83,643
112,311
133,097
122,360
120,222
Humber Estuary
121,417
104,213
128,117
129,926
113,202
119,375
Somerset Levels
181,156
76,790
93,386
88,701
102,726
108,552
Breydon Water and Berney Marshes
93,666
91,014
96,523
88,857
91,413
92,295
Alt Estuary
107,806 64,034 87,950 78,759 73,792
82,468
Ouse Washes
103,761 63,938 63,088 101,941 75,902
81,726
Montrose Basin
79,064
81,591 76,509 77,483 61,677 98,060
76,970
Mersey Estuary
56,443
93,696
62,347
88,453
83,910
Severn Estuary
75,630
83,603
75,151
74,834
71,453
76,134
Blackwater Estuary
63,830
68,017
66,111
83,696
91,090
74,549
75,957
69,930
74,156
57,819
64,038
68,380
Strangford Lough
72,761 78,759 60,881 65,256 43,337
64,199
Hamford Water
41,485 41,404 63,372 62,228 52,570
52,212
Dengie Flats
61,801 49,715 45,021 55,842 46,460
51,768
Swale Estuary
76,768 54,773 57,012 36,358 29,352
50,853
Stour Estuary
52,096 50,276 44,520 48,735 52,699
49,665
Chichester Harbour
53,167 47,769 41,661 47,518 50,207
48,064
Loughs Neagh and Beg
40,696 49,692 45,100 46,828 49,043
46,272
Loch of Strathbeg
46,063 38,960 39,388 29,364 72,936
45,342
Forth Estuary
Inner Moray and Beauly Firths
37,070 42,064 41,643 46,202 42,532
41,902
Loch Leven
32,724 39,979 37,629
41,268
Lindisfarne
45,109 47,878 36,519 30,334
60,774 35,236 44,048
40,778
Burry Inlet
27,943
38,500
47,254
29,972
46,863
38,106
Carmarthen Bay
61,010
33,868
26,519
21,347
30,646
34,678
Abberton Reservoir
29,515
45,634
23,725
35,059
37,613
34,309
Alde Estuary
35,024
32,994
31,011
32,988
36,643
33,732
Cromarty Firth
31,582
33,678
34,210
31,993
35,172
33,327
Loch of Skene
28,693 19,658 35,718 29,946 50,149
32,833
Lower Derwent Ings
39,020 38,105 29,914
32,331
27,911 26,704
Langstone Harbour
26,791
36,893
30,025
32,217
27,957
30,777
WWT Martin Mere
24,897
30,330
22,672
41,861
31,340
30,220
35,560
28,688
28,886
29,076
25,432
29,528
Colne Estuary
15,667 31,616 30,213 26,889 41,136
29,104
Lough Foyle
20,733 26,917 32,437 34,309 31,106
29,100
Dornoch Firth
33,277 32,215 24,996 23,789 29,363
28,728
Crouch-Roach Estuary
30,283 26,087 22,881 24,595 29,958
26,761
Dungeness and Rye Bay
Nene Washes
42,456
12,455
24,812
27,718 26,037 26,696
Medway Estuary
33,459 27,014 14,589 28,876 22,477
25,283
Pegwell Bay
22,893 30,562 43,813 18,503 10,009
25,157
Rutland Water
26,282 33,633 16,539 28,702 18,537
24,739
Orwell Estuary
24,068 21,377 22,155
25,283 26,121
23,801
Carsebreck and Rhynd Lochs
20,749 22,584 24,024
22,632 25,183
23,034
West Water Reservoir
16,658
18,794
20,254
28,200
29,600
-
-
-
-
21,975
21,975
17,074
21,662
23,272
22,807
24,673
21,898
22,736 26,494 17,902 20,833 16,414
20,876
Colwyn and Penrhyn Bays Poole Harbour Cleddau Estuary
Duddon Estuary Exe Estuary
19,302
21,292
18,723
20,316 18,623 19,154
22,701
25,395
20,748
22,003 22,368
20,493
19,028
• Totals are the sum of species maxima during the WeBS-year at each site, using data from all months. This summary does not account for missed visits or reduced coverage. • Some totals may differ slightly from those published in previous annual WeBS reports. • Non-native species (such as Canada Goose and Ruddy Duck), are excluded, as are gulls and terns due to incomplete coverage. • A more comprehensive table showing all sites supporting more than 10,000 waterbirds is available online via www.bto.org/webs.
14 BoCC4
Birds of Conservation Concern 4 An overview of changes in the conservation status of wetland bird species in the UK, Channel Islands and Isle of Man 300
For species that regularly breed in Britain, assessments of non-breeding data (including WeBS population trends) were only carried out if there is also a substantially separate nonbreeding population of the species. Assessments of 25-year trends covered the 1986/87–2011/12 period and used smoothed index values. Long-term trend assessments used data from 1966/67 for wildfowl and 1974/75 for waders.
WADERS
The WeBS trend for over-wintering Curlew has declined since 2000; however, it is the evidence of declines in UK breeding populations which has led to the Red listing of Curlew (previously on the Amber list). As a result of this decline, together with Curlew’s European and Global “Near Threatened” status, and the international importance of the UK population, Curlew has been called “the most pressing bird conservation priority in the UK” (Brown et al., 2015). Lapwing, Whimbrel, Black-tailed Godwit, Ruff and Red-necked Phalarope remain on the Red list
WeBS Index
200
100
0 75/76
85/86
95/96
05/06
15/16
75/76
85/86
95/96
05/06
15/16
150
100 WeBS Index
The 2015 review of the status of bird species in the UK, Channel Islands and Isle of Man, Birds of Conservation Concern 4 is the fourth such report since the first conservation status lists were produced in 1996 (Eaton et al., 2015). Non-breeding population trend information from the Wetland Bird Survey and the Goose and Swan Monitoring Programme formed important evidence for the species assessments, together with other information such as global threat according to the IUCN Red List and breeding population trends from the BTO/JNCC/RSPB Breeding Bird Survey.
50
0
WeBS indices for newly red-listed species Ringed Plover (top) and Curlew (bottom). Green dots = annual population index; blue line = smoothed trend.
due to declines in their breeding population and/or range and are joined by Dotterel and Woodcock. Ringed Plover has been moved up to the Red list due to severe nonbreeding decline over 25 years: numbers have decreased by 52%. Conversely, Dunlin moved from the Red list to the Amber list as its long-term decline fell just short of the 50% threshold, at 49%. Greenshank, Sanderling and Curlew Sandpiper move from the Green list, joining thirteen other wader species remaining on the Amber list. Only four wader species remain on the Green list.
SEA DUCKS AND GREBES Red listed Scaup and Common Scoter are joined by Long-tailed
Duck from the Green list and Velvet Scoter, Red-necked Grebe and Slavonian Grebe from the Amber list. Long-tailed Duck, Velvet Scoter and Slavonian Grebe are classified as globally “Vulnerable” under IUCN Red List criteria. The WeBS 1992/93 to 2011/12 trend (earliest available data) for Red-necked Grebe has decreased by 72%.
WILDFOWL
As forecast in its Species Focus in Waterbirds in the UK 2011/12, Pochard has been Red listed due to a 51% decline in the WeBS 25-year trend. Its longer term trend shows a decline of 34%. White-fronted Goose is now Red listed at the species level as well both UK races (European and Greenland) as the
BOCC4 15
Table 3 Status of waterbirds in BoCC4
r - species on Red list previously, a - species on the Amber list previously and g - species on Green list previously
smoothed index decreased by 60% over 25 years. Mute Swan joined the Amber list due to the internationally important UK population.
Golden Plover had previously been Amber listed due to the estimated international importance of the UK population (over 20% of that of the East Atlantic Flyway). Little Grebe was Green listed after the latest assessment from UK breeding surveys. The rapid expansion in UK breeding Little Egrets saw this species too changing from Amber to Green status.
500 400
WeBS Index
Results from the latest 2015 European Red List of Birds assessment resulted in Red-throated Diver, Little Gull, Black Tern, Jack Snipe and Tufted Duck all moving to the Green BOCC4 list, signifying they are of lesser conservation concern, although in some cases the move was due to changes in the European Red List assessment process rather than a genuine improvement in birds' status.
600
300 200 100 0 65/66
75/76
85/86
95/96
05/06
15/16
400
300
WeBS Index
CURLEW BY DAVE KING; EUROPEAN WHITE-FRONTED GOOSE BY GRAHAM CATLEY; RINGED PLOVER BY JILL PAKENHAM; POCHARD BY NEIL CALBRADE
GREEN-LISTED SPECIES
700
200
100
0 65/66
75/76
85/86
95/96
05/06
15/16
WeBS indices for newly red-listed species White-fronted Goose(top) and Pochard (bottom). Green dots = annual population index; blue line = smoothed trend.
FIND OUT MORE... Brown, D., Wilson, J., Douglas, D., Thompson, P., Foster, S., McCulloch, N., Phillips, J., Stroud, D., Whitehead, S., Crockford, N., & Sheldon, R. 2015. The Eurasian Curlew – the most pressing bird conservation priority in the UK? British Birds 108: 660–668. Eaton, M., Aebischer, N., Brown, A., Hearn, R., Lock, L., Musgrove, A., Noble, D., Stroud, D. & Gregory, R. 2015. Birds of Conservation Concern 4: the population status of birds in the UK, Channel Islands and Isle of Man. British Birds 108: 708–746.
16 Habitat Focus... Natural Inland Still Water
Birds of lakes and ponds A look at the status and trends of three species closely associated with still freshwater Natural Inland Still Water as a WeBS habitat category encompasses a huge variety of areas of open freshwater waterbird habitats, from ponds, tarns and small lakes to the UK’s largest freshwater lakes – Lough Neagh in Northern Ireland, Loch Lomond in Scotland, Windermere in England and Llyn Tegid in Wales. Inland still water occurs throughout the UK, including on many small islands, but local geology and conditions influence the types of natural waterbodies and their attractiveness to different waterbird species. Most of the larger deeper lakes are glacial in origin and found in north and western Britain and Northern Ireland. These oligotrophic waterbodies attract relatively small numbers of ducks and grebes but can be important roost sites for gulls and geese. Higher concentrations of waterbirds can be found in the lowlands, particularly in base-rich areas of chalk or limestone which support greater plant and invertebrate life for the birds to feed on. Meres (shallow lakes) are important for swans, geese and dabbling ducks such as Shoveler and Gadwall. Some ephemeral pools, meres and turloughs regularly disappear due to rainfall variations or fluctuations in the water table, but can still attract waterbirds while present. As with all wetland habitats, WeBS coverage is most complete for the largest wetlands in the lowlands and near major population centres. However, when aggregated, small upland tarns and lochans and lowland ponds and lakes hold considerable numbers of dispersed waterbirds such as Mallard, Teal and Goosander; so counts from these are particularly useful for refining population estimates (see pages 26–27).
Open water is an important component of several important wetland complexes designated for their waterbirds, such as Broadland Special Protection Area (SPA). Several of the larger mesotrophic and eutrophic lakes such as Loch Leven and Hornsea Mere support internationally important concentrations of waterbirds and have SPA status. The fortunes of the species cited for individual SPAs can be compared in the WeBS Alerts section of WeBS Report Online (see page 5). The Numbers
& Trends section allows the exploration of the importance of natural inland still water for Mute Swan, Goldeneye, Mallard, Coot and many other WeBS species by selecting the appropriate option in the habitat drop down on species' pages.
LLANGORSE LAKE BY KEITH NOBLE
Habitat Focus... Natural Inland Still Water 17
Natural inland still waters such as Llangorse Lake attract a wide variety of waterbird species.
18 Habitat Focus... Natural Inland Still Water
TUFTED DUCK
The aptly named Tufted Duck congregates in flocks of hundreds of birds on some of our largest lakes, but is also widely dispersed at much smaller waterbodies. It is correspondingly one of the most widely recorded species in the Wetland Bird Survey and was observed at 2,586 individual WeBS count sectors (49%) at 1,735 sites (62%) in 2014/15.
NEIL CALBRADE
The largest aggregations are recorded at Loughs Neagh and Beg in Northern Ireland and Loch Leven in Scotland. Many of the other sites which hold numbers of Tufted Duck greater than the nationally important thresholds for this species are large artificial waterbodies: reservoirs and gravel pits in southern Britain (Table 4).
The WeBS index trend for Great Britain has increased almost threefold since 1966/67, but has been stationary in the past four years. However, changes are occurring in the wintering distribution across the flyway.
The rapid breeding colonisation of Britain by Tufted Duck from the mid1800s is believed to have been aided by the introduction of the non-native Zebra Mussel in 1825.
There have been decreases in France and in Ireland, including Northern Ireland where the WeBS trend declined by a third between the mid-1990s and mid-2000s (although numbers appear to have stabilised now).
As can be inferred from the monthly indices, the resident UK and Ireland population is augmented in winter by birds from abroad; ringing recoveries suggest many birds which breed in Iceland migrate to Ireland whilst many wintering visitors to south-east England breed in Fennoscandia and north-west Russia.
Scandinavia, where early winter temperatures increased 3.8â °C between 1980 and 2010, has seen corresponding increases in
150
150
100
WeBS Index
WeBS Index
100
50
0 65/66
the number of wintering Tufted Ducks. The number of Tufted Ducks in Finland increased by almost 20% a year over 30 years, estimated to result in an increase of over 100,000 birds wintering in Finland and Sweden; read more about the situation in Finland on pages 24–25.
70/71
75/76
80/81
85/86
90/91 95/96
00/01
05/06
10/11
15/16
WeBS trend for Tufted Duck in UK. Green dots = annual population index; blue line = smoothed trend.
50
0
Jul
Aug
Sep
Oct
Nov
Dec
Jan
Feb
Mar
Apr
May
Jun
Monthly indices for Tufted Duck in UK. Green bars = 2014/15; blue line/hatched area = previous 5-year mean/range.
Habitat Focus... Natural Inland Still Water 19
Table 4 Nationally important sites for Tufted Duck Site
2010/11
2011/12
2012/13
2013/14
2014/15
Month
5-year mean
Loughs Neagh and Beg
8,078
9,009
8,547
7,682
6,526
Jan
Loch Leven
6,455
(7,193)
5,863
11,614
5,657
Oct
7,968 7,397
Rutland Water
5,449
7,692
4,984
6,114
3,560
Sep
5,560
Abberton Reservoir
2,790
2,872
2,075
2,729
2,874
Oct
2,668
Chew Valley Lake
2,420
2,100
2,475
2,100
2,355
Sep
2,290
Ouse Washes
1,548
665
3,933
1,916
2,912
Feb
2,195
Upper Lough Erne
2,836
2,348
1,451
1,354
2,152
Dec
2,028 2,002
Hanningfield Reservoir
1,596
1,866
1,465
2,454
2,628
Aug
1,815
1,645
1,421
1,937
2,031
Dec
1,770
1,490
1,978
1,725
562
1,693
Aug
1,490
1,164
1,492
1,104
1,434
2,218
Sep
1,482
Cotswold Water Park (West) 1,429
1,470
1,599
1,230
1,378
Feb
1,421
1,469
Nov
1,408
Grafham Water Walthamstow Reservoirs Pitsford Reservoir Wraysbury Gravel Pits
1,214
1,260
1,510
1,585
Lee Valley Gravel Pits
1,409
1,453
1,097
1,244
Little Paxton Gravel Pits 707 1,563 547 879 • Five-year mean is for period 2010/11 to 2014/15. • Threshold for sites of national importance = 1,100 (Great Britain), 310 (All-Ireland).
1,183
Nov
1,277
2,617
Oct
1,263
20 Habitat Focus... Natural Inland Still Water
MOORHEN
150
Moorhens have a widespread distribution throughout the UK and occur in a wide variety of wetland habitats, notably including small ponds and ditches.
In 2014/15, the counted British maximum for Moorhen at 14,349 was similar to that of recent years, with the highest site maxima during the year being 344 at Severn Estuary in February.
MUTE SWAN
Like Tufted Duck and Moorhen, Mute Swan is a widely dispersed species, more numerous in the lowlands. Due to its history as a semi-domestic species, it is a species often found near human habitation. The population increase in the 1980s and 1990s is attributed to the recovery of Mute Swan populations after the ban in 1987 of most sizes of lead fishing weights. Since 2000, annual indices have been steady; in the most recent years, a slight decline in 2012/13 and 2013/14 has been somewhat reversed in 2014/15. Mute Swans in Britain and Ireland are largely sedentary, and hence the populations are considered separate from both one another and from birds on the Continent. Consequently, sites of national importance in Britain and AllIreland importance in Northern Ireland are recognised as being of
WeBS Index
0 95/96
00/01
05/06
10/11
15/16
WeBS trend for Moorhen in UK. Green dots = annual population index; blue line = smoothed trend.
international importance. The absence of a migratory component to the wintering population, unusual among WeBS species, results in mirrored trends from the Breeding Bird Survey and WeBS - implying the larger waterbodies included in WeBS are representative for this species. Whilst successful pairs of Mute Swans often remain on their breeding territories to moult and throughout the winter, non-breeders and immature birds often form herds
(Rowell and Spray, 2004). As sites can fall in and out of favour with winter herds, at the site level there is a mixed picture. Internationally important sites with recent declines include Rutland Water in the Midlands and the Stour Estuary in Essex. However, the Welsh side of the Severn Estuary continued recent increases in peak WeBS counts with a record number 345 birds in August. The largest natural lake in the West Midlands – Aqualate Mere
120 20,000 100
80
15,000
60 10,000 40 5,000 20
0 1966
1976
1986
1996
2006
0
CBC/BBS and mean winter WeBS count for Mute Swan in UK 1966-2014. Left axis - CBC/BBS index: blue line = CBC/BBS index smoothed trend, pale blue = CBC/BBS 85% confidence interval, Blue dots = CBC/BBS annual index values. Right axis - Green line = WeBS smoothed trend and Green dots = mean WeBS count.
Total WeBS count
The UK breeding trend for this species is volatile, with numbers dropping after hard winters. Moorhen was added to the WeBS scheme in 1993/4 and the WeBS trend indicates that numbers at WeBS sites had been declining for a decade, but the index for 2014/15 is the highest since 2009/10 – perhaps in response to recent milder winters.
50
BBS Index
Unlike Tufted Duck, they do not congregate in large numbers but remain dispersed all year, including wintering visitors. Consequently Moorhens are relatively poorly monitored by WeBS and there are no sites containing nationally (or internationally) important numbers.
100
Habitat Focus... Natural Inland Still Water 21
Table 5 Internationally important sites for Mute Swan Site
2010/11
2011/12
2012/13
2013/14
2014/15
Month
5-year mean
Loughs Neagh and Beg
951
857
851
1,050
1,101
Sep
962
Somerset Levels
951
1,074
823
869
1,072
Dec
958
Fleet and Wey
922
774
743
695
799
Dec
787
Loch Leven
428
665
685
524
686
Jul
598
Upper Lough Erne
650
440
399
692
722
Oct
581
Rutland Water
637
542
497
396
403
Sep
495
Ouse Washes
437
247
749
505
436
Dec
475
Stour Estuary
575
586
473
393
294
Nov
464
428
549
465
479
390
Aug
462
481
398
509
420
437
Oct
449
Severn Estuary
334
368
365
365
500
Aug
386
Loch of Harray
320
357
394
368
368
Jan
361
Tweed Estuary
456
390
228
314
360
Aug
350
298
215
458
437
282
Aug
338
245 150 217 144 152
Oct
182
Nov
158
Abberton Reservoir Loch Bee (South Uist)
Loch of Strathbeg Lower Lough Erne Strangford Lough
186
123
195
• Five-year mean is for period 2010/11 to 2014/15. • Threshold for International importance = 320 (British Population), 100 (Irish population).
– has seen numbers increase from under 10 birds in the 1960s and 1970s. With counts only reaching three figures for the first time in 2011, in 2014/15 the peak WeBS count was an impressive 387 birds. Some internationally important sites have peaks in mid-winter, such as the Somerset Levels where the December WeBS count of 1,072 was the highest in Britain in 2014/15, and at Fleet and Wey with a December peak of 799. Others see their maxima earlier in the WeBS year - the highest WeBS count in 2014/15 was at Loughs Neagh and Beg in Northern Ireland, where 1,101 swans were recorded in September. The highest Scottish site WeBS count of 686 was at Loch Leven in July, a traditional moulting site for the species.
FIND OUT MORE...
TONI CROSS
Rowell, H.E. & Spray, C.J. 2004. The Mute Swan Cygnus olor (Britain and Ireland populations) in Britain and Northern Ireland 1960/61–2000/01. Waterbird Review Series, The Wildfowl & Wetlands Trust/Joint Nature Conservation Committee, Slimbridge.
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100
22 International
East Atlantic Flyway monitoring Latest results from monitoring coastal waterbird populations reveal declines in benthivore species
Coastal waterbirds migrating along the East Atlantic Flyway ecologically connect the high Arctic with southern Africa. The coastal wetlands of western Europe and Africa are critical to many species of the Flyway. A consortium of the Wadden Sea Flyway Initiative, Wetlands International and BirdLife International, co-operating with national bird wintering and breeding monitoring schemes such as WeBS, enables reporting at the Flyway scale: essential context for understanding local and national data.
Cooperation following the East Atlantic Flyway Monitoring Strategy has improved the availability of data for western Africa by incorporating historical count data in to the International Waterbird Census database and coordinating counting efforts (supported by WeBS and other organisations; see the article in WeBS News Issue 30).
ENVIRONMENTAL CHANGE The report notes that of the 66 East Atlantic Flyway populations assessed, 35% show an increasing trend and 35% a decreasing trend over the 2003–2014 period, suggesting both positive and negative drivers from environmental change. Of the assessed Flyway populations,
VOGELBESCHERMING NEDERLAND
Status of coastal waterbird populations in the East Atlantic Flyway 2014 reports on population sizes and trends (van Roomen et al., 2015). The primary data source was the International Waterbird Census for wintering waterbirds (including January WeBS counts from the UK). Data from the Pan-European Common Bird Monitoring Scheme (including WBBS/BBS data from the UK) was available for four species of waterbird included in the report: Redshank, Curlew, Whimbrel and Black-headed Gull. The East Atlantic Flyway.
40 occur in internationally important numbers in the Wadden Sea, an important intertidal site along the coasts of parts of the Netherlands, Denmark and Germany. Of these, a high proportion of the fish-eating (piscivore) species demonstrated increasing population trends. However, most benthivore species that feed on shellfish, crabs, worms and other invertebrates have declining trends – and this was especially true of species that have high proportions of populations using the Wadden Sea. It was estimated that the total number of benthivores along the Flyway decreased by 2.5 million birds between 2003 and 2014.
FIND OUT MORE... van Roomen, M., Nagy, S., Foppen, R., Dodman, T., Citegetse, G., & Ndiaye, A. 2015. Status of coastal waterbird populations in the East Atlantic Flyway 2014. With special attention to flyway populations making use of the Wadden Sea. Leeuwarden, The Netherlands. www.waddensea-secretariat.org/ management/publications/status-ofcoastal-waterbird-populations-in-theeast-atlantic-flyway-2014
International 23
Redshank
Curlew Sandpiper 1,200
140
1,000
1,000
800
800
number x1,000
number x1,000
100 80 60 40
600 400
600
200
20 0
number x1,000
1,200
120
0
1980 1985 1990 1995 2000 2005 2010
400 200 0
1980 1985 1990 1995 2000 2005 2010
1980 1985 1990 1995 2000 2005 2010
Benthivore species (n=29) Piscivore species (n=7) 0%
25% Increasing
Sandwich Tern
50% Stable
75% Decreasing
Spoonbill 120
100
12
100
80
10
80
60
40 20 0
Index
number x1,000
14
8 6
20
2 1980 1985 1990 1995 2000 2005 2010
60 40
4 0
100%
Cormorant
120
number x1,000
REDSHANK BY AL DOWNIE, CURLEW SANDPIPER BY TOMMY HOLDEN, OYSTERCATCHER BY JOHN HARDING, SANDWICH TERN BY JILL PAKENHAM, SPOONBILL BY AMY LEWIS, CORMORANT BY JOHN HARDING
Oystercatcher
160
1980 1985 1990 1995 2000 2005 2010
0
1980 1985 1990 1995 2000 2005 2010
The proportion of increasing, stable and decreasing flyway trends in 2003-2014 of benthivore and piscivore populations for which the Wadden Sea is an important staging or wintering area. Individual flyway trends are shown for benthivore species Redshank, Curlew Sandpiper, Oystercatcher and piscivore species Sandwich Tern, Spoonbill and Cormorant (from van Roomen et al., 2015).
24 Another National Scheme
Diving ducks on the rise in Finland Aleksi Lehikoinen introduces the waterbird monitoring scheme in Finland Monitoring of wintering birds has long traditions in Finland. The Finnish Museum of Natural History has coordinated winter bird counts since 1956/57. In winter bird counts all birds, including waterbirds, are counted along freely chosen line transects (c. 10 km long), but the museum has coordinated routes so they are not overlapping. Traditionally Finnish coastal waters used to be mainly covered by ice, but due to climate change, water areas especially in the south-west archipelago remains nowadays ice free and have become suitable wintering areas for waterbirds. Due to these historical reasons winter bird counts have been the main Finnish contribution to the International Waterbird Counts (IWC). Other additional IWC surveys include three shipborne surveys and the first aerial surveys were started
report weather conditions, crop size of rowan berries and in recent years sex ratios of observed species if possible (since 2010).
in the winter of 2015/16. In the winter bird counts, the survey effort has been relatively constant between 423 and 632 routes annually for more than 50 years.
The recent trend analyses show that waterbirds, especially diving ducks such as Tufted Duck, Goldeneye and Smew have increased rapidly (more than 40 fold increases in these species) and simultaneously wintering numbers on the southern edge of the flyway in Central Europe, such as Ireland, France and Switzerland have decreased.
There are three census seasons: 1–15 November (counted since 1975), 25 December to 7 January (since winter 1956/57) and 21 February to 6 March (since 1967). The mid-winter counts are more popular than the two other seasons. The counts are done by volunteers (c. 1,000 observers annually), often in small groups. Habitats of the counted birds as well as the amount of habitat along the routes is measured using eight categories: a) dumping ground or fur farm; b) urban settlement; c) rural settlement; d) arable land; e) forest; f ) clear-cut area or stand of saplings; g) reed-bed or shore scrub; and h) other. The last category includes birds in wetlands. The observers are also asked to
Climate change will likely increase abundance of wintering waterbirds in Finnish waters as larger water areas remain ice free. Understanding the context of these changes has required redevelopment of the monitoring program, and also international collaboration to understand the local changes in wintering numbers along the flyway.
64
FIND OUT MORE...
32
Fraixedas Nuñez, S., Lehikoinen, A. & Lindén, A. 2015. Impact of climate and land change on wintering bird populations in Finland. Journal of Avian Biology 46: 63–72.
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Relative abundance of 10 common waterbird species in Finland - Whooper Swan, Mallard, Tufted Duck, Long-tailed Duck, Goldeneye, Goosander and Black-headed, Common, Herring and Great Black-backed Gulls (from Fraixedas et al. 2015). Only positive error bars of 95% confidence intervals are shown.
Lehikoinen, A., Jaatinen, K., Vähätalo, A., Clausen, P., Crowe, O., Deceuninck, B., Hearn, R., Holt, C. A., Hornman, M., Keller, V., Nilsson, L., Langendoen, T., Tománková, I., Wahl, J. & Fox, A. D. 2013. Rapid climate driven shifts in wintering distribution of three waterbird species. Global Change Biology 19: 2071–2081.
GRAHAM CATLEY
Another National Scheme 25
Goldeneye numbers in Finland have increased rapidly as larger water areas now remain ice free in the winter.
26 Stratified Population Estimates
Stratified population estimates A new approach for estimating waterbird populations using information about the distribution of wetland habitats One of the principal aims of WeBS is to “assess the size of non-breeding waterbird populations in the UK”. In the latest estimates of overwinter waterbird population in Great Britain, Musgrove et al. (2011) recommended that there should be continued development into population estimation methods for species in the wider countryside, away from the large wetlands that are regularly counted for WeBS. Méndez et al. (2015) used WeBS data to investigate whether environmental data could help inform population estimates for nineteen widely dispersed waterbird species of inland wetlands.
STRATIFYING BRITAIN BY WETLAND HABITATS Great Britain was divided into 5x5 km squares, each assigned to a wetland environmental stratum depending on whether the square had: • low or high proportion of urban land cover; • colder or milder mean winter temperature than the GB average; • upland or lowland habitats; • high or low amounts of still
freshwater; • high or low still freshwater complexity; and • linear freshwater eatures which were canals/drains or rivers. Of the 64 possible combinations, there were examples of 62 strata. The freshwater variables were determined using a Principal Component Analysis. This allowed just three summary variables to capture most of the variation in ten separate inland wetland variables: total lake area; number of lakes; mean lake area; largest lake area; mean lake perimeter; longest lake perimeter; river length; drain length; canal length; and coast length. The figure opposite shows which wetland measurements contributed to the three components.
STRATIFIED POPULATION ESTIMATES The use of stratified wintering population estimates was recommended for six species. The estimates for Teal, Tufted Duck and Coot were higher than the published estimates, which are based on simple extrapolation of
WHY ARE POPULATION ESTIMATES NEEDED? • The UK and Ireland are particularly important for waterbird populations due to the mild climate, strategic position on the East Atlantic Flyway and productive coastal and inland wetlands. • High concentrations of overwintering waterbirds means UK data is also very important for estimating European and World waterbird populations of some species. • Thresholds for identifying sites of national importance and international importance for species compare numbers at the site with national and international population estimates. Identifying sites regularly supporting important numbers is crucial for protecting wetland habitats.
WeBS counts. However, the authors suggest that the extrapolation factors used previously may be too low, given how widespread the species are (for example, see the Tufted Duck map, page 19). This approach would increase the Teal population estimate from 210,000 to 388,000; the Tufted Duck estimate from 110,000 to 133,500 and the Coot estimate from 180,000 to 237,000. The Canada Goose stratified estimate is smaller than the published estimate, at 167,000 rather than 190,000. This is a species that appears to be expanding more rapidly into small water habitats such as drainage ditches in the wider countryside. These are less well represented in WeBS counts, which may be affecting the stratified estimate. The Mute Swan stratified estimate is also smaller than the published estimate, at 58,000 rather than 74,000 birds. However this is perhaps more in keeping with the breeding Mute Swan census estimate of 31,700 individuals. The sixth species was Great Crested Grebe, where the published estimate of 19,000 birds overlaps the 95% confidence interval of the stratified population estimate, 16,100– 19,100. The stratified habitat approach only estimates inland individuals. To account for birds on the coast, it may be possible to use the approach developed for Cormorant (Chamberlain et al., 2013), where coastal and inland estimates are combined, for Great Crested Grebe and possibly also other species with coastal populations such as Goldeneye.
Stratified Population Estimates 27
Still freshwater Low/High Mean, total and largest lake area and mean, total and longest lake perimeter
Complexity Low/High Total number of lakes and total lake perimeter compared to lake area
Linear features Drains/Rivers Length of drains and/or coast compared to length of rivers
Examples of high and low scoring areas for the three freshwater principal components.
VALUE OF COUNTS FROM SMALLER SITES In general, the stratified population estimates tended to be higher than the published estimates for species that are widely dispersed, yet have a significant proportion of their population on a few sites, such as Gadwall, Shoveler and Pintail. They tended to be lower for species with a more uniform distribution such as Grey Heron, Mallard and Moorhen. The most influential strata for satisfactory modelling of dispersed waterbird populations tended to be mild lowland regions with urban areas. Two influential strata were particularly under-represented by WeBS Counts, both with riverine features. One is the class of cold, rural, upland 5 km squares with low amounts of still water and low freshwater complexity. The other contains mild, lowland, urban areas,
also with relatively low amounts of still water; but what there is, is relatively complex. WeBS prioritises regular survey of sites with large concentrations of waterbirds, as the information from these sites is crucial for estimating waterbird trends and populations for many species and for protecting important sites. However, counters of small wetlands make a vital contribution to improved estimates of populations of dispersed species such as Teal and Coot. Méndez et al. (2015) suggest that improved coverage of small waterbodies and rivers could also enable more accurate estimation of widespread unobtrusive species such as Moorhen and Little Grebe.
FIND OUT MORE... Chamberlain, D.E., Austin, G.E., Green, R.E., Hulme, M.F., & Burton, N.H.K. 2013. Improved estimates of population trends of Great Cormorants Phalacrocorax carbo in England and Wales for effective management of a protected species at the centre of a human-wildlife conflict. Bird Study 60: 335–344. Musgrove, A.J., Austin, G.E., Hearn, R.D., Holt, C.A., Stroud, D.A., & Wotton, S.R. 2011. Overwinter population estimates of British waterbirds. British Birds 104: 364–397. Méndez, V., Austin, G.E., Musgrove, A.J., Ross-Smith, V.H., Hearn, R.D., Stroud, D. A., Wotton, S.R. & Holt, C.A. 2015. Use of environmental stratification to derive non-breeding population estimates of dispersed waterbirds in Great Britain. Journal for Nature Conservation 28: 56–66.
28 Species Focus...Scarcer Wintering Waders
Increasing numbers of some scarcer wintering wader species Some wader species traditionally seen on passage are wintering in increasing numbers in recent years
Feb), Chichester Harbour (52, Nov) the Tamar Complex (51, Feb) and Taw-Torridge Estuary (41, Nov). Outside of the winter months, the peak passage occurs in September (England) and October (Wales and Scotland) when birds are migrating south; the peak autumn count was at Chichester Harbour (96, Sep).
WHIMBREL
RUFF: DAVE KING
Whimbrel have a pronounced passage through the UK in spring and autumn, with a small breeding population in northern Scotland. Between 1 November 2014 and 31 March 2015, 49 records were received through WeBS, from 16 sites in Britain and one in Northern Ireland (Outer Ards). In Britain, most records were from the south coast, though interestingly, two were recorded at Borron Point on the Solway Estuary in November 2014. Winter numbers ranged from 1–3, with Chichester Harbour (Central) and Bury Marsh at Southampton Water each recording a peak of three, both on 8 November. The long-
GREENSHANK
If we are lucky, and depending on where we go birdwatching, we may encounter one of the less common wintering wader species such as Whimbrel, Greenshank, Spotted Redshank and Ruff. Scarcer still are Little Stint and Curlew Sandpiper which tend to peak in August or September, but just a few remain to over-winter.
The number of Greenshank present during winter in the UK has increased over the last two decades, probably at least in part due to milder climatic conditions. There were 721 observations of Greenshank recorded between 1 November 2014 and 31 March 2015 with peak counts recorded at Strangford Lough (59,
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November to March WeBS trend for Whimbrel in UK. Green dots = annual population index; blue line = smoothed trend.
WHIMBREL: DAVE WRAGG
Species Focus...Scarcer Wintering Waders 29
term pattern in November to March numbers suggests an increase.
years. A total of 185 records were received for the period November 2014 to March 2015, with peak counts at Lower Derwent Ings (131, Dec), North Norfolk Coast (124, Nov), Ouse Washes (84, Feb) and WWT Martin Mere (78, Jan).
records with peak counts at Humber Estuary (12, Nov) and North Norfolk Coast (10, Nov).
SPOTTED REDSHANK
RUFF
The winter trend for Spotted Redshank is now similar to mid 1970s, though there was a distinct peak in the late 1990s, after which numbers dropped again. Peak months are March and October, during the main passage periods; the peak count for 2014/15 was at Old Hall Marshes in the Blackwater Estuary (60, Oct). In the 2014/15 winter months November–March we received 143
After a marked increase in winter Ruff numbers at WeBS sites during the 1990s and early 2000s, there was a downward trend until 2011/12, after which the trend shows an increase again. This is primarily a passage species, with the peak months being March and September; breeding was last confirmed in 2012, though lekking has been recorded in recent
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The winter trends shown by WeBS suggests that these scarce wintering waders are either stable or increasing in number; although the reasons for this are unclear, but milder winter climatic conditions may be a strong influence.
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30 Species Focus...Bar-tailed Godwit
Globe-trotting Godwits Bar-tailed Godwits are globally widespread with several subspecies migrating huge distances along the flyways Coastal in its winter habits, the Arctic-breeding Bar-tailed Godwit is found on estuaries around the UK. Peak numbers of between 11,000 and 22,000 occur on the Wash and aggregations of several thousand birds are recorded by WeBS in mid-winter on other estuarine sites around the UK coast. Five-year mean peak counts currently exceed national or international importance thresholds at twenty-six sites. The 40-year UK trend for Bartailed Godwit is steady in the long-term with fairly large interPeak month 2014/15 (July – June) J A S O N D J F M A M J Mean peak numbers 2010/11–2014/15 1 – 150 151 – 380 (All-Ireland National Threshold) 381 – 1,220 (GB National Threshold) 1,201 – 17,247 (International Threshold)
year variability and a possible cyclic pattern of typically 5-7 years between peaks. The annual index peaked at 1.7 times the current level in 1996/7 and a minimum of 86% of current numbers was seen in 2005/06. There was an apparent decline in the index from the turn of the millennium onwards but this has been somewhat reversed in recent years. The lapponica subspecies of Bar-tailed Godwit breeds in Fennoscandia and winters mostly in the UK and the Netherlands
but also reaches as far south as the Iberian peninsula. It increased in numbers between 1988 and 2003 and has since stabilised (Nagy et al., 2014). The taymyrensis sub-species breeds in central Siberia and “leap-frogs” the lapponica population, migrating along the flyway in spring and autumn to spend mid-winter in west and south-west Africa. Although based on limited data, there is a suggestion that this subspecies is declining (van Roomen et al., 2015). The peak count on most of the Bar-tailed Godwit's major UK sites is December and the WeBS month index likewise usually peaks midwinter. Counts on other WeBS sites are often highest in other months and the peak reporting rate for this species in BirdTrack, as measured by the proportion of birdwatchers’ complete lists each week recording the species, peaks in September with a secondary peak in early May. This may relate to additional taymyrensis passage migrants occurring more widely across the country, as well as passage movement of lapponica individuals that over-wintered more locally.
FIND OUT MORE... Nagy, S., Flink, S., & Langendoen, T. 2014. Waterbird trends 1988–2012: Results of trend analyses of data from the International Waterbird Census in the African-Eurasian Flyway. Ede, The Netherlands. van Roomen, M., Nagy, S., Foppen, R., Dodman, T., Citegetse, G., & Ndiaye, A. 2015. Status of coastal waterbird populations in the East Atlantic Flyway 2014. With special attention to flyway populations making use of the Wadden Sea. Leeuwarden, The Netherlands.
NEIL CALBRADE
Species Focus...Bar-tailed Godwit 31
Bar-tailed Godwits have the longest known non-stop migratory flight of any bird. One satellite tagged individual flew 11,680 km (7,258 miles) from Alaska to New Zealand without stopping. 180
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Population trend of Bar-tailed Godwit (lapponica race) wintering in the East Atlantic Flyway based on January IWC counts.
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32 Species Focus...Crane
NEIL CALBRADE
Focus on... Crane
It is claimed that no other wild bird appears in so many British places names as the Crane. There is also archaeological and documentary evidence that it was once a wellknown bird in Britain as a breeder, as well as a wintering visitor, as far north as Orkney (Boisseau & Yalden, 1998). There are now welcome signs of a comeback for this charismatic bird, slowly regaining its place in the British wetland avifauna. The WeBS winter index has increased rapidly in the past six years, although counters at only a favoured few sites are fortunate enough to record the species routinely. Extinct as an Irish breeding bird since c.1300s and as a British breeding bird since c.1600, sightings became very rare as the Crane declined across Europe. Thankfully in the 20th century continental populations began to recover, resulting in annual British records from the early 1950s onwards. A particularly notable influx
of around 500 birds along the south coast was recorded in late autumn 1963, in response to cold weather (Stanbury, 2011).
and disperse widely to feed on grazing marsh and surrounding arable fields. In recent years, a wintering flock has built up in the East Anglian fens.
There are currently four main centres of population, with the British breeding birds largely sedentary. The oldest population centre is in the Broads of East Anglia, where a pair arrived in autumn 1979, stayed, and bred in 1981. Breeding has taken place here every year since. Breeding has also taken place in Yorkshire since 2002, in the East Anglia fens since 2007 and north-east Scotland since 2012. There is a known link between birds in the East Anglian fens and Broads but it is unknown whether individuals in Yorkshire and Scotland originated from the Broads population.
Winter WeBS Core Counts see Cranes most regularly recorded at St Benet’s Levels, Nene Washes and Lakenheath Fen, Severn Estuary and Somerset Levels and Thorne Moors WeBS sites.
Stanbury (2011) notes the Broads wintering population to be over 40 birds, but that, as the population has increased, accurate counting is more difficult as birds do not all roost together
FIND OUT MORE...
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Boisseau, S. & Yalden D.W. 1998. The former status of the Crane Grus grus in Britain. Ibis 140: 482–500.
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Due to the low productivity and slow natural spread from east England, the Great Crane Project aimed to double the British population. Between 2010 and 2015, 93 birds from German stock were raised and released in the Somerset Levels. A higher proportion of these reintroduced birds have been captured in monthly WeBS counts, explaining the recent very rapid increase in the index. Now these releases have ended, it will be very interesting to see whether the Crane population index will continue to increase.
Stanbury, A. 2011. The changing status of the Common Crane in the UK. British Birds 104: 432–447.
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WWT, RSPB, Pensthorpe Conservation Trust and Viridor Credits. 2015. Great Crane Project Annual Report 2014– 2015. www.thegreatcraneproject.org. uk/news/annual-reports
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Species Focus...Shoveler 33
NEIL CALBRADE
Focus on... Shoveler
Shoveler is a highly migratory species that responds rapidly to local environmental factors of food availability and temperature. In winter it favours shallow freshwater and flooded meadows but can also be found in brackish marshes and estuaries. Shoveler favours wintering in warmer conditions than other regularly occurring dabbling duck species, with the mean temperature experienced by European populations in January being around 9⁰C, compared with 4 – 8⁰C for Wigeon, Gadwall, Teal and Pintail and around 3⁰C for the hardy Mallard (Dalby et al., 2013). Shoveler are sensitive to freezing conditions which prevent feeding. As a specialist feeder of freshwater invertebrates, Dalby et al. (2013) speculated that higher crustacean densities associated with warmer water temperatures also influence Shoveler European distribution.
Guillemain et al. (2000) found that food abundance is of crucial importance for winter habitat selection, and that if zooplankton density decreased at a site over winter then Shovelers moved on from the site. The UK WeBS index includes passage migrants and overwintering birds from eastern Europe and Russia. In the 1950s UK maxima were in February and March whereas in the 1960s and 1970s numbers declined throughout the winter after a November peak. More recently the trend is for birds to be present in more equal numbers throughout the September – March period, although in keeping with Shoveler mobility in response to conditions, there is variation from year to year. Nine sites surpassed the threshold for international importance with a fiveyear mean peak of over 400 birds.
Most sites with nationally important numbers of Shoveler are in England. The Welsh side of the Severn and Llynnau Y Fali in Anglesey are the only non-English sites qualifying in Great Britain. The index for Northern Ireland more than halved between 2002/03 and 2012/13, but numbers appear to have started to recover in the past two years, a pattern mirrored in both sites with numbers above the Irish national threshold. Strangford Lough had the highest total since 2009/10 with 104 birds and Loughs Neagh and Beg the highest since 2007/08 with 72 birds.
FIND OUT MORE...
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Guillemain, M., Fritz, H. & Guillon, N. 2000. Foraging behavior and habitat choice of wintering Northern Shoveler in a major wintering quarter in France. Waterbirds 23: 353–363.
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Dalby, L., Fox, A.D., Petersen, I.K., Delany, S., & Svenning, J.C. 2013. Temperature does not dictate the wintering distributions of European dabbling duck species. Ibis 155: 80–88.
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Four of these had maxima greater than their five-year mean. After a record peak at Abberton Reservoir in 2013/14 of 2,031 birds, the 2014/15 maxima of 651 in August was the lowest for six years. Conversely, at the Somerset Levels, the peak of just 2,020 in January 2015 was the highest since 2007/08.
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34 Low Tide Counts
UK Low Tide Counts 2014/15 Sixteen UK estuaries were counted at low tide, generating important data about feeding areas counted at low tide once every six years, although on some sites more frequent counts are undertaken.
Information collected at low tide represents an important contribution to the conservation of waterbirds, by providing supporting information for the management of UK Ramsar Sites and Special Protection Areas, other site designations, and whole estuary conservation plans. On most estuaries, numbers of waterbirds feeding on predefined sectors of inter-tidal habitat are counted. Most individual estuaries are
Presentation of WeBS low tide information typically takes two forms: (i) tabulated statistics of peak numbers and mean densities, and (ii) dot density maps to give a visual representation of species’ foraging densities across a site. Dots do not represent the precise positions of birds; they are assigned to habitat components proportionally and placed randomly within those areas. No information about
Coordinated counts of waterbirds are made each month from November to February inclusive, in the two-hour period either side of low tide. Each counted sector is divided into a maximum of three distinct habitat components: inter-tidal, sub-tidal, and nontidal. Species data are divided among these habitats depending on the habitat preferences of the species concerned.
distribution of birds at a finer scale than the count sector level should be inferred. For all maps on the online reporting interface, one dot is equivalent to one bird. During 2014/15, WeBS Low Tide Counts were carried out at 16 estuaries. These included the Dee Estuary, Alt Estuary, Hamford Water and Portsmouth Harbour, all of which were counted for the first time since 2008/09. Results from the counts at Portsmouth Harbour are presented on pages 36–37 of this report. Further information about WeBS Low Tide Counts, including data summaries and distribution maps for different estuaries and species, are available online via www.bto. org/websreporting-lowtide.
SANDERLING: JILL PAKENHAM
The WeBS Low Tide Count scheme facilitates the collection of information about use of the UK’s estuaries by waterbirds at low tide. The scheme has flourished since its inception in the winter of 1992/93, with all the major estuaries in the UK having been counted at least once. The scheme aims to monitor, assess and regularly update information on the relative importance of inter-tidal feeding areas of UK estuaries for wintering waterbirds, and in doing so complements information gathered through the WeBS Core Counts.
Low Tide Counts 35
1) 2) 3) 4) 5) 6) 7) 8) 9) 10) 11) 12) 13) 14) 15) 16)
Loch Fleet Breydon Water Orwell Estuary Stour Estuary Hamford Water Adur Estuary Pagham Harbour Langstone Harbour Portsmouth Harbour Swansea Bay Burry Inlet Dee Estuary Alt Estuary Wyre Estuary Kent Estuary Strangford Lough
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Estuaries in the UK counted as part of WeBS Low Tide Count scheme in 2014/15.
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36 Low Tide Counts
Portsmouth Harbour at low tide Most sites are counted on a cyclical basis enabling comparison of data between years This large harbour in the Solent lies between Portsmouth to the east, and Gosport and Fareham to the west. The main freshwater inflow is Wallington River to the northwest. This meets the saltwater at Fareham Lake, which restricts the freshwater input to the Harbour. The connection to the Solent is only 200 metres wide at the narrowest point. Saltmarsh is a relatively limited habitat around the shores of the estuary. However, eelgrass and algal growth on the mudflats is more extensive. The shores of the harbour are heavily industrialised, including port and housing developments, along with major naval docks and installations. Future developments and dock expansion may impact the site; the pressure to reduce MOD activity/spending could lead to the release of land adjacent to the
Harbour for development (D. Bill pers. comm.).
Forton Lake whereas in 2008/09 they were more widely distributed.
The distribution of two species are mapped on the opposite page. For Dark-bellied Brent Goose and Black-tailed Godwit, distributions based on WeBS Low Tide Counts undertaken in 2008/09 are displayed for comparison with the respective distributions from 2014/15.
Black-tailed Godwit is another species that has shown a long-term increase in the UK population. Despite this national increase, between 2008/09 and 2014/15, the mean winter low tide counts at Portsmouth Harbour almost halved from 249 birds (0.42 birds per ha), in 2014/15 compared to 481 (0.81 birds per ha) in 2008/09. The largest concentrations in both winters were in Fareham Lake and Paulsgrove Lake.
Dark-bellied Brent Geese are present in internationally important numbers in Portsmouth Harbour with a five-year average of 2,578 birds. The mean winter counts at low tide in Portsmouth Harbour have remained stable with 2,204 (1.44 birds per ha) in 2008/09, compared to 2,238 (1.42 birds per ha) in 2014/15. The largest concentrations of Darkbellied Brent Geese in 2014/15 were in Paulsgrove Lake, Tipner Lake and
GENERAL STATISTICS FOR PORTSMOUTH HARBOUR Area covered: 968 ha Mean total birds: 9,739 Mean bird density: 10.1 birds per ha
1.42
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Mean densities of waterbirds at low tide at Portsmouth Harbour in 2014/15.
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Low Tide Counts 37
DARK-BELLIED BRENT GOOSE BY GRAHAM CATLEY; BLACK-TAILED GODWIT BY JOHN HARDING
Dark-bellied Brent Goose
Black-tailed Godwit
Low tide distribution of Dark-bellied Brent Goose (1 dot = 2 birds) and Black-tailed Godwit (1 dot = 1 bird) at Portsmouth Harbour, for the winters of 2014/15 (red) and 2008/09 (blue).
38 WeBS Data Requests
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Uses of WeBS data 2014/15
A summary of site-based WeBS information is presented on the online interface, but data at a finer level (both spatial and temporal) are available in a user-friendly format through a bespoke WeBS Data Request. Any WeBSbased information that is to be incorporated into site evaluation work, such as Environmental Impact Assessments (EIAs), should be sourced through a WeBS Data Request to ensure the data have been validated and summarised appropriately. The graph shows the number of Data Requests processed by the WeBS office each year since 2008/09. These are from a range of stakeholder groups, including country conservation agencies, environmental consultancies, academic researchers and bird clubs. Summarised WeBS data are also provided to several online environmental data portals.
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With the UK host to internationally important numbers of overwintering waterbirds, one of the principal aims of WeBS is to provide data to facilitate their conservation. Indeed, there have been many high-profile examples over the years in which WeBS data have proved to be fundamental in securing the protection of important wetland sites.
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January WeBS data are supplied to Wetlands International for inclusion in the International Waterbird Census, and summaries are used in outputs such as waterbird population estimates, and AEWA Conservation Status reports. The WeBS Partnership is keen to encourage WeBS data use within environmental research. A number of scientific papers and reports that have used WeBS data in recent years are referenced within the pages of this annual report, and there is of course an extensive suite of other research questions relating to waterbird ecology
and wider wetland management issues to which WeBS data would lend themselves, at both national and international scales. Academic researchers, students and potential collaborators interested in using WeBS data can email the WeBS office at webs@bto.org.
WeBS DATA REQUESTS More information about the WeBS Data Request Service is available from www.bto.org/webs-data where you can see coverage by WeBS of different sites, check data request charges, and view examples of the data that can be provided.
WeBS Local Organisers 39
WeBS Local Organisers in 2014/15
Selected further reading
Continued from back page
Recent studies that have used WeBS data
WALES
Anglesey Breconshire Burry Inlet Caernarfonshire Caernarfonshire (Foryd Bay) Cardigan (incl Dyfi Estuary) Carmarthenshire Clwyd (coastal) Clwyd (inland) East Glamorgan Gwent (excl Severn Estuary) Merioneth (estuaries) Merioneth (other sites) Montgomeryshire Pembrokeshire Radnorshire Severn Estuary (Wales) West Glamorgan
NORTHERN IRELAND Antrim (Larne Lough) Antrim (other sites) Armagh (excl Loughs Neagh and Beg) Belfast Lough Down (Carlingford Lough) Down (Dundrum Bay) Down (other sites) Down (Outer Ards) Down (South Down Coast) Down (Strangford Lough) Fermanagh Londonderry (Bann Estuary) Londonderry (Lough Foyle) Londonderry (other sites) Loughs Neagh and Beg Tyrone (excl Loughs Neagh and Beg)
CHANNEL ISLANDS Alderney Channel Islands (inland) Guernsey Coast Jersey Coast
Ian Sims Andrew King Lyndon Jeffery Rhion Pritchard Simon Hugheston-Roberts Russell Jones Terry Wells VACANT Duncan Halpin Daniel Jenkins-Jones Al Venables Jim Dustow Trefor Owen Jane Kelsall Annie Haycock Peter Jennings Al Venables Lyndon Jeffery
Doreen Hilditch Adam McClure Stephen Hewitt Shane Wolsey Shane Wolsey Patrick Lynch Shane Wolsey NIEA Shane Wolsey Kerry Mackie Michael Stinson Hill Dick Matthew Tickner Shane Wolsey NIEA Vacant (now Michael Stinson)
Alderney Wildlife Trust Ecologist Glyn Young Mary Simmons Roger Noel
ISLE OF MAN Isle of Man
Pat Cullen
We would be grateful for help organising WeBS in areas currently without a Local Organiser (marked VACANT). If you live in one of these areas and would be interested in taking on the role, please let us know. Email: webs@bto.org. In 2014/15, the WeBS Local Organiser Advisory Committee (WeBS LOAC) comprised John Armitage, Neil Bielby, Gladys Grant, Andrew King, Nick Mason, Brian Moore, Dave Shackleton and Shane Wolsey. Many thanks to them for representing the wider LO network. Further information about the WeBS LOAC can be found at www.bto. org/webs/loac.
WeBS ONLINE REPORT Further information, including site tables and trends for all the regular WeBS species, is available in the online report at www.bto.org/webs-reporting.
Holt, C.A., Austin, G.E., Calbrade, N.A., Mellan, H.J., Hearn, R.D., Stroud, D.A., Wotton, S.R. & Musgrove, A.J. 2015. Waterbirds in the UK 2013/14: The Wetland Bird Survey. BTO/RSPB/JNCC. BTO, Thetford. Austin, G.E. & Burton, N.H.K. 2014. Notes on the WeBSDefra Annual Cormorant Index. BTO Research Report 678. BTO, Thetford. Austin, G.E. 2015. The Use of Wetland Bird Survey (WeBS) Data for Rapid Condition Assessment of Non-Breeding Waterbird SPAs in England. Research Report 670. BTO, Thetford. Cook, A.S.C.P., Barimore, C., Holt, C.A., Read, W.J. & Austin, G.E. 2013. Wetland Bird Survey Alerts 2009/10: Changes in numbers of wintering waterbirds in the UK, SPAs and SSSIs. BTO Research Report 641. http://blx1.bto.org/ webs-reporting-alerts. Eaton, M.A., Aebischer, N.J., Brown, A.F., Hearn, R.D., Lock, L., Musgrove, A.J., Noble, D.G., Stroud, D.A., & Gregory, R.D. 2015. Birds of Conservation Concern 4: the population status of birds in the UK, Channel Islands and Isle of Man. British Birds 108: 708–746. Fox, A.D., Dalby, L., Christensen, T.K., Nagy, S., Balsby, T.J.S., Crowe, O., Clausen, P., Deceuninck, B., Devos, K., Holt, C., Hornman, M., Keller, V., Lehikoinen, A., Lorentsen, S.-H., Molina, B., Nilsson, L., Stipniece, A., Svenning , J.-C. & Wahl, J. 2016. Seeking explanations for recent changes in abundance of wintering Eurasian Wigeon (Anas penelope) in northwest Europe. Ornis Fennica 93:12–25. Hayhow D.B., Bond A.L., Eaton M.A., Grice P.V., Hall C., Hall J., Harris S.J., Hearn R.D., Holt C.A., Noble D.G., Stroud D.A. & Wotton S. 2015. The state of the UK’s birds 2015. RSPB, BTO, WWT, JNCC, NE, NIEA, NRW and SNH, Sandy, Bedfordshire. www.bto.org/SUKB. Méndez, V., Austin, G.E., Musgrove, A.J., Ross-Smith, V.H., Hearn, R.D., Stroud, D.A., Wotton, S.R., & Holt, C.A. 2015. Use of environmental stratification to derive nonbreeding population estimates of dispersed waterbirds in Great Britain. Journal for Nature Conservation 28: 56–66. Pavón-Jordán, D., Fox, A.D., Clausen, P., Dagys, M., Deceuninck, B., Devos, K., Hearn, R.D., Holt, C.A., Hornman, M., Keller, V., Langendoen, T., Ławicki, Ł., Lorentsen, S.H., Luigujõe, L., Meissner, W., Musil, P., Nilsson, L., Paquet, J.Y., Stipniece, A., Stroud, D.A., Wahl, J., Zenatello, M., & Lehikoinen, A. 2015. Climate-driven changes in winter abundance of a migratory waterbird in relation to EU protected areas. Diversity and Distributions 21: 571–582. Pearce-Higgins, J.W. & Holt, C.A. 2013. Impacts of climate change on waterbirds. Marine Climate Change Impacts Partnership Science Review 2013: 149–154. Robinson, R.A., Marchant, J.H., Leech, D.I., Massimino, D., Sullivan, M.J.P., Eglington, S.M., Barimore, C., Dadam, D., Downie, I.S., Hammond, M.J., Harris, S.J., Noble, D.G., Walker, R.H. & Baillie, S.R. 2015. BirdTrends 2015: trends in numbers, breeding success and survival for UK breeding birds. BTO Research Report 678. BTO, Thetford. www.bto.org/ birdtrends. Ryan, L.J. Green, J.A. & Dodd, S.G. 2016. Weather conditions and conspecific density influence survival of overwintering Dunlin Calidris alpina in North Wales. Bird Study 63: 1–9.
SPECIAL THANKS We wish to thank all surveyors and Local Organisers for making WeBS the success it is today. Unfortunately space does not permit all observers to be acknowledged individually, but we would especially like to credit the Local Organisers for their efforts.
WeBS Local Organisers in 2014/15 ENGLAND
in association with
British Trust for Ornithology The Nunnery Thetford Norfolk IP24 2PU 01842 750050 webs@bto.org www.bto.org/webs
Avon (excl Severn Estuary) Bedfordshire Berkshire
Rupert Higgins Richard Bashford Ken White
Buckinghamshire (North) Buckinghamshire (South) Cambridgeshire (incl Huntingdonshire) Cambridgeshire (Nene Washes) Cambridgeshire (Ouse Washes) Cheshire (North) Cheshire (South) Cleveland (excl Tees Estuary) Cleveland (Tees Estuary) Cornwall (excl Tamar Complex) Cornwall (Tamar Complex) Cotswold Water Park Cumbria (Duddon Estuary) Cumbria (excl estuaries) Cumbria (Irt/Mite/Esk Estuary) Dee Estuary Derbyshire Devon (other sites) Devon (Exe Estuary) Devon (Taw/Torridge Estuary) Dorset (excl estuaries) Dorset (Poole Harbour) Dorset (Radipole and Lodmoor) Dorset (The Fleet and Portland Harbour) Durham Essex (Crouch/Roach Estuaries and South Dengie) Essex (Hamford Water) Essex (North Blackwater) Essex (other sites) Essex (South Blackwater and North Dengie) Gloucestershire Greater London (excl Thames Estuary) Greater Manchester Hampshire (Avon Valley) Hampshire (estuaries/coastal) Hampshire (excl Avon Valley) Herefordshire Hertfordshire Humber Estuary (inner South) Humber Estuary (mid South) Humber Estuary (North) Humber Estuary (outer South) Isle of Wight Kent (Dungeness area) Kent (East) Kent (North Kent estuaries) Kent (Pegwell Bay) Kent (West) Lancashire (East Lancs and Fylde) Lancashire (North inland) Lancashire (Ribble Estuary) Lancashire (River Lune) Lancashire (West inland) Lee Valley Leicestershire and Rutland (excl Rutland Water)
Chris Coppock VACANT Bruce Martin
Leicestershire and Rutland (Rutland Water) Lincolnshire (North inland) Lincolnshire (South inland) Merseyside (Alt Estuary) Merseyside (inland) Merseyside (Mersey Estuary) Morecambe Bay (North) Morecambe Bay (South) Norfolk (Breydon Water) Norfolk (excl estuaries) Norfolk (North Nofolk Coast)
Tim Appleton
Northamptonshire (excl Nene Valley) Northamptonshire (Nene Valley) Northumberland (coastal) Northumberland (inland) Northumberland (Lindisfarne) Nottinghamshire Oxfordshire (North)
Charlie Kitchin Paul Harrington Kane Brides David Cookson Chris Sharpe Mike Leakey Pete Roseveare Gladys Grant Gareth Harris Colin Gay Dave Shackleton Peter Jones Colin Wells Peter Gibbon Pete Reay Penny Avant Brian O'Leary Malcolm Balmer Paul Morton Toby Branston Steve Groves VACANT Peter Mason Julian Novorol John Thorogood Gavin Foster Anthony Harbott Michael Smart Helen Baker Jamie Dunning John Clark John Shillitoe Keith Wills Chris Robinson Jim Terry Keith Parker Richard Barnard Nick Cutts John Walker Jim Baldwin David Walker Norman McCanch Geoff Orton Ian Hodgson Norman McCanch Stephen Dunstan Peter Marsh Ken Abram Jean Roberts Tom Clare Cath Patrick Brian Moore
Chris Gunn Bob Titman Steve White Kevin Feeney Dermot Smith VACANT Jean Roberts Jim Rowe Tim Strudwick Michael Rooney (now Neil Lawton) VACANT Steve Brayshaw Daniel Turner (now Kathy Evans) Steve Holliday Andrew Craggs David Parkin Sandra Bletchly
Oxfordshire (South) Severn Estuary (England) Shropshire Solway Estuary (inner South) Solway Estuary (outer South) Somerset (other sites) Somerset (Somerset Levels) Staffordshire Suffolk (Alde Complex) Suffolk (Alton Water) Suffolk (Blyth Estuary) Suffolk (Deben Estuary) Suffolk (Orwell Estuary) Suffolk (other sites) Suffolk (Stour Estuary) Surrey Sussex (Chichester Harbour) Sussex (other sites) Thames Estuary (Foulness) The Wash Warwickshire West Midlands Wiltshire Worcestershire Yorkshire (East and Scarborough) Yorkshire (Harrogate and Yorkshire Dales) Yorkshire (Huddersfield/Halifax area) Yorkshire (Leeds area) Yorkshire (South) Yorkshire (Wakefield area)
SCOTLAND
Ben Carpenter Harvey Rose Michael Wallace Norman Holton Dave Shackleton Eve Tigwell Steve Meen Steve Turner (now Scott Petrek) Ian Castle John Glazebrook Adam Burrows (now Will Russell) Nick Mason Mick Wright Alan Miller Rick Vonk Penny Williams James Parkin Richard Bown (now Helen Crabtree and Dave Boddington) Chris Lewis Jim Scott Matthew Griffiths Nick Lewis Bill Quantrill Andrew Warr Jim Morgan Bill Haines VACANT Paul Morris Jamie Dunning Peter Smith
Aberdeenshire Angus (excl Montrose Basin) Angus (Montrose Basin) Argyll Mainland Arran Ayrshire Badenoch and Strathspey Borders Bute Caithness
Vacant (now Moray Souter) VACANT Anna Cheshier Paul Daw Jim Cassels Dave Grant Keith Duncan Andrew Bramhall Ian Hopkins Sinclair Manson
Central (excl Forth Estuary) Clyde Estuary Dumfries and Galloway (Auchencairn and Orchardtown Bays) Dumfries and Galloway (Fleet Bay) Dumfries and Galloway (Loch Ryan) Dumfries and Galloway (other sites) Dumfries and Galloway (Rough Firth) Dumfries and Galloway (Wigtown Bay) Fife (excl estuaries) Fife (Tay and Eden Estuaries) Forth Estuary (inner) Forth Estuary (outer North) Forth (outer South) Glasgow/Renfrewshire/Lanarkshire Harris and Lewis Islay, Jura and Colonsay
Neil Bielby John Clark Euan MacAlpine David Hawker Paul Collin Andy Riches Judy Baxter Paul Collin
Allan Brown Norman Elkins Michael Bell Alastair Inglis Duncan Priddle John Clark Yvonne Benting John Armitage (now David Wood) Isle of Cumbrae VACANT Lochaber John Dye Lothian (excl estuaries) Allan Brown Lothian (Tyninghame Estuary) Bobby Anderson Moray and Nairn (inland) David Law Moray and Nairn (Lossie Estuary) Bob Proctor Moray Basin Coast Bob Swann Mull Paul Daw Orkney Eric Meek (now Morag Wilson) Perth and Kinross (excl Loch Leven) Michael Bell Perth and Kinross (Loch Leven) Jeremy Squire Shetland Paul Harvey Skye and Lochalsh Robert Macmillan Solway Estuary (North) Andy Riches Sutherland (excl Moray Basin) VACANT Tiree and Coll John Bowler Uists and Benbecula Yvonne Benting West Inverness/Wester Ross Vacant (now Andy Douse)
ISBN 978-1-908581-66-2